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Attachment D - Stormwater and Water Quality report
garden/accessible soil); 109mg/kg of copper; and 1220 mg/kg of zinc. All impacted material occurs at shallow depth (0-200mm) in fill material present across the lot, and attenuates rapidly with depth, with all the (200-500mm) samples collected from natural insitu soils at these locations reporting metal concentrations below the EILs. Lot 1 RP87371: Metal concentrations in excess of Qld EPA EILs remain onsite (as shown on Figure 3), with maximum concentrations being: 112mg/kg of arsenic (also above HIL “A” guidelines); 143mg/kg of copper; 148mg/kg of chromium (III); and 884 mg/kg zinc. Although there is no nominated guideline for boron, two samples collected from this allotment also reported concentrations of boron in excess of the acknowledged background concentrations (maximum concentration detected was 723mg/kg). All impact occurs in samples collected at shallow depth (0-200mm) in fill material present across the lot, however in some locations the impact has not been vertically delineated. Lot 5 SP173771: In the area to the east and south east of the former boiler building (as shown on Figure 4) metal concentrations in excess of Qld EPA commercial/industrial health based investigation levels (HIL “F”) guidelines remain onsite, with maximum concentrations detected being: 8820mg/kg of arsenic; 8930mg/kg of copper; and 30400mg/kg of chromium. This impact occurs at shallow depth (0-200mm) in fill material present in this area of the lot, however in one location it has not been vertically delineated. Although no nominated guideline exists for boron, these samples also reported concentrations of boron in excess of the acknowledged background concentrations (maximum concentration detected was 9410mg/kg). In other areas of Lot 5, metal concentrations in excess of Qld EPA EILs remain onsite, with maximum concentrations detected in other areas of the site being: 60mg/kg for arsenic, and 131mg/kg for chromium(III). All impacted material occurs at shallow depth (0-200mm) in fill material, however in some areas the impact has not been vertically delineated. Lot 7 SP173771 Areas of residual soil impact across this lot are shown in Figure 5. Residual soil impact in locations F2 and F3 exceeds Qld EPA EILs for arsenic, copper and chromium (IIT). As part of soil remediation works undertaken at the site in the year 2000, this area was capped by a 500mm clay layer. This clay capping layer has a confirmed density ratio of 95.5%. This capping layer was covered by 100mm of clean soil. Residual soil impact in the location of the former evaporation pond exceeds Qld EPA HIL”F” levels for arsenic, and the EILs for copper and chromium (III). As part of soil remediation works undertaken at the site in 2000, this area was backfilled with soil excavated during the replacement of the causeway at the site, the soil excavated from behind the boiler as part of other soil remediation works onsite, and imported clay fill. This backfill was then capped by a 500mm clay layer. Sections of this clay capping
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